JP5526502B2 - Exhaust gas purification catalyst and method for producing the same - Google Patents

Exhaust gas purification catalyst and method for producing the same Download PDF

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JP5526502B2
JP5526502B2 JP2008185189A JP2008185189A JP5526502B2 JP 5526502 B2 JP5526502 B2 JP 5526502B2 JP 2008185189 A JP2008185189 A JP 2008185189A JP 2008185189 A JP2008185189 A JP 2008185189A JP 5526502 B2 JP5526502 B2 JP 5526502B2
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compound
noble metal
exhaust gas
gas purifying
purifying catalyst
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JP2010022910A (en
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一幸 白鳥
雅紀 中村
広憲 若松
克雄 菅
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Nissan Motor Co Ltd
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Priority to PCT/JP2009/060221 priority patent/WO2010007839A1/en
Priority to CN2009801275390A priority patent/CN102099111B/en
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    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
    • F01N3/24Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by constructional aspects of converting apparatus
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Description

本発明は、内燃機関から排出される排気ガスを浄化する処理に適用して好適な排気ガス浄化用触媒及びその製造方法に関する。   The present invention relates to an exhaust gas purifying catalyst suitable for a process for purifying exhaust gas discharged from an internal combustion engine, and a method for manufacturing the same.

近年、内燃機関から排出される排気ガス中に含まれる炭化水素系化合物(HC)、一酸化炭素(CO)、窒素酸化物(NO)等の有害物質を除去するために、アルミナ(Al)等の金属酸化物担体に白金(Pt)等の貴金属粒子を担持した排気ガス浄化用触媒が広く利用されるようになっている。従来の排気ガス浄化用触媒では、周囲の雰囲気変動に対する貴金属粒子の耐久性を向上させるために、貴金属粒子が多量に用いられている。しかしながら、貴金属粒子を多量に用いることは地球資源保護の観点から見ると望ましくない。 In recent years, in order to remove harmful substances such as hydrocarbon compounds (HC), carbon monoxide (CO), and nitrogen oxides (NO x ) contained in exhaust gas discharged from an internal combustion engine, alumina (Al 2 Exhaust gas purifying catalysts in which noble metal particles such as platinum (Pt) are supported on a metal oxide carrier such as O 3 ) are widely used. In conventional exhaust gas purification catalysts, a large amount of noble metal particles is used in order to improve the durability of the noble metal particles against ambient fluctuations. However, using a large amount of noble metal particles is not desirable from the viewpoint of protecting earth resources.

貴金属の使用量を低減するには、担体に担持された貴金属粒子の粒子径を小さくすることがある。貴金属粒子の粒子径が小さいほど、比表面積が大きくなるから、所望の触媒浄化性能を得るための貴金属の使用量は少なくて済む。しかしながら、貴金属粒子の粒子径が小さいと、高温や長時間使用により互いに熱凝集(シンタリング)をしてしまうため、耐久性が低下するおそれがある。   In order to reduce the amount of noble metal used, the particle diameter of the noble metal particles supported on the carrier may be reduced. The smaller the particle size of the noble metal particles, the larger the specific surface area. Therefore, the amount of noble metal used for obtaining the desired catalyst purification performance can be reduced. However, if the particle diameter of the noble metal particles is small, they may be thermally agglomerated (sintered) with each other due to high temperatures or long-term use, which may reduce durability.

そこで、貴金属粒子が第1の化合物に担持され、この貴金属粒子を担持した第1化合物が第2の化合物に内包されて、当該貴金属が担持された第1の化合物同士がこの第2の化合物により隔てられた構造を有する排気ガス浄化用触媒が開発された(特許文献1)。このような構造を有する排気ガス浄化用触媒は、貴金属粒子が第1の化合物に担持されることにより、第1の化合物に貴金属粒子が物理的に固定されることにより、貴金属粒子の移動凝集が抑制され、かつ、この貴金属粒子を担持した第1の化合物が、第2の化合物によって互いに隔てられることで、この貴金属を担持した第1の化合物が互いに接触し凝集することを抑制する。これらのことにより、貴金属粒子が耐久後に凝集することを防止して耐久性を向上させることができる。
国際公開第2007/052627号パンフレット
Therefore, the noble metal particles are supported on the first compound, the first compound supporting the noble metal particles is encapsulated in the second compound, and the first compounds supporting the noble metal are supported by the second compound. An exhaust gas purification catalyst having a separated structure has been developed (Patent Document 1). In the exhaust gas purifying catalyst having such a structure, the noble metal particles are supported on the first compound, and the noble metal particles are physically fixed to the first compound. The first compounds supported by the noble metal particles are separated from each other by the second compound, so that the first compounds supporting the noble metal are prevented from contacting and aggregating with each other. By these things, durability can be improved by preventing the noble metal particles from aggregating after durability.
International Publication No. 2007/052627 Pamphlet

特許文献1に記載された排気ガス浄化用触媒は、貴金属粒子を担持する第1の化合物が、Ceを主成分とした酸化物からなる。そのため、この従来の排気ガス浄化用触媒は、空気−燃料比率(空燃比)が理論空燃比(ストイキオメトリー)を中心としてリッチ−リーン間の雰囲気変動が周期的に起こるような条件下での排気ガスの浄化の場合には、このCeを主成分とする酸化物が有している酸素吸放出能により触媒粒子近傍の雰囲気が変動するのを緩和することができ、これにより貴金属のシンタリングの抑制、及び三元反応に必要な活性酸素の供給が適切に行われ、高い浄化性能を有する。いては製造コストや環境負荷を大きくすることなく、第1の化合物による貴金属粒子の活性向上効果を維持することができる。 In the exhaust gas purifying catalyst described in Patent Document 1, the first compound supporting noble metal particles is made of an oxide containing Ce as a main component. For this reason, this conventional exhaust gas purifying catalyst has an air-fuel ratio (air-fuel ratio) under a condition where a rich-lean atmosphere fluctuation periodically occurs centering on the stoichiometric air-fuel ratio (stoichiometry). In the case of exhaust gas purification, it is possible to mitigate the fluctuation of the atmosphere in the vicinity of the catalyst particles due to the oxygen absorption / release capability of the oxide containing Ce as a main component, thereby enabling the sintering of precious metals. Suppression of oxygen and supply of active oxygen necessary for the three-way reaction are appropriately performed, and high purification performance is achieved. Is not shed without increasing the production cost and environmental load, it is possible to maintain the effect of enhancing the activity of the noble metal particles by the first compound.

しかしながら、空気−燃料比率が化学量論比よりもリーン側で運転されるガソリン直噴エンジンやディーゼルエンジンに、上述の排気ガス浄化用触媒を適用した場合には、貴金属の酸化が生じ、排気ガス浄化性能が低下することがあった。   However, when the above-mentioned exhaust gas purification catalyst is applied to a gasoline direct injection engine or a diesel engine that is operated on the lean side of the stoichiometric ratio of the air-fuel ratio, noble metal oxidation occurs and the exhaust gas Purification performance may be reduced.

上記課題を解決するために、本発明に係る排気ガス浄化用触媒は、貴金属と、第1の化合物と、第2の化合物からなり、前記貴金属は当該第1の化合物に担持され、前記貴金属が担持された第1の化合物は当該第2の化合物に内包されて、当該貴金属が担持された第1の化合物同士が前記第2の化合物により隔てられた構造のユニットを含み、かつ、
前記貴金属はPtからなり前記第1の化合物はTiを主成分とし、かつ、TiO 、TiO −ZrO 複合化合物又はTiO −CeO 複合化合物からなり、前記第2の化合物は[Al及びSi]から選ばれる1つ以上を主成分とすることを要旨とする。
In order to solve the above problems, the exhaust gas purifying catalyst according to the present invention, a noble metal, a first compound, made from a second compound, the noble metal is supported on the first compounds, the noble metal the first compound supported is encapsulated in the second compound, the first compound in which the noble metal is supported with each other includes a unit structure separated by the second compound, and,
The noble metal consists Pt, wherein said first compound is mainly composed of Ti, and consists TiO 2, TiO 2 -ZrO 2 complex compound or TiO 2 -CeO 2 composite compound, the second compound is [ The main point is that the main component is one or more selected from Al and Si.

また、本発明に係る排気ガス浄化用触媒の製造方法は、上記の排気ガス浄化用触媒を製造する方法であって、貴金属が接触した第1の化合物を、1次粒子径が100nm以下のコロイド状にする工程と、次いで、コロイド状にした当該貴金属が接触した第1の化合物の周囲に、第2の化合物を形成させる工程とを含むことを要旨とする。   The method for producing an exhaust gas purifying catalyst according to the present invention is a method for producing the above exhaust gas purifying catalyst, wherein the first compound in contact with the noble metal is converted into a colloid having a primary particle diameter of 100 nm or less. And a step of forming a second compound around the first compound in contact with the colloidal noble metal.

また、本発明に係る排気ガス浄化用触媒の製造方法は、上記の排気ガス浄化用触媒を製造する方法であって、第1の化合物の2次粒子集合体を微粒化して、貴金属が接触した第1の化合物の2次粒子径を2μm以下にする工程と、次いで、微粒化した当該貴金属が接触した第1の化合物の周囲に、第2の化合物を形成させる工程とを含むことを要旨とすることもできる。   The method for producing an exhaust gas purifying catalyst according to the present invention is a method for producing the above exhaust gas purifying catalyst, wherein the secondary particle aggregate of the first compound is atomized and the noble metal comes into contact. Including a step of setting the secondary particle diameter of the first compound to 2 μm or less and a step of forming a second compound around the first compound in contact with the atomized noble metal. You can also

本発明に係る排気ガス浄化用触媒によれば、直噴エンジンやディーゼルエンジンのように空気燃料比率が化学量論比よりもリーン側で運転するエンジンに用いた場合に、優れた排気ガス浄化性能を有している。   The exhaust gas purification catalyst according to the present invention has excellent exhaust gas purification performance when used for an engine that operates on the lean side of the stoichiometric ratio, such as a direct injection engine or a diesel engine. have.

本発明の排気ガス浄化用触媒の製造方法によれば、上記の効果を有する本発明の排気ガス浄化用触媒を、容易に製造することができる。   According to the method for producing an exhaust gas purification catalyst of the present invention, the exhaust gas purification catalyst of the present invention having the above effects can be easily produced.

以下、本発明の排気ガス浄化用触媒の実施形態について、図面を用いつつ説明する。   Hereinafter, embodiments of an exhaust gas purifying catalyst of the present invention will be described with reference to the drawings.

図1は、本発明の一実施形態となる排気ガス浄化用触媒の模式図である。同図に示す排気ガス浄化用触媒1は、触媒活性を有する貴金属粒子2と、この貴金属粒子2と接触し、当該貴金属粒子2の移動を抑制する第1の化合物3と、この貴金属粒子2と第1の化合物3とを内包し、当該貴金属粒子2の移動を抑制すると共に第1の化合物3同士の接触に伴う第1の化合物3の凝集を抑制する第2の化合物4とからなる。この第1の化合物3は、貴金属粒子2を担持している。また、貴金属粒子2を担持した第1の化合物3の複数個の集合体が、第2の化合物4により隔てられた区画内に含まれている。   FIG. 1 is a schematic diagram of an exhaust gas purifying catalyst according to an embodiment of the present invention. The exhaust gas purifying catalyst 1 shown in FIG. 1 has a noble metal particle 2 having catalytic activity, a first compound 3 that contacts the noble metal particle 2 and suppresses the movement of the noble metal particle 2, and the noble metal particle 2. The second compound 4 includes the first compound 3 and suppresses the movement of the noble metal particles 2 and suppresses the aggregation of the first compound 3 due to the contact between the first compounds 3. The first compound 3 carries noble metal particles 2. In addition, a plurality of aggregates of the first compounds 3 carrying the noble metal particles 2 are included in the compartments separated by the second compounds 4.

このような構造の排気ガス浄化用触媒1は、貴金属粒子2と、第1の化合物3とが接触して、担持することにより第1の化合物3が化学的結合のアンカー剤として作用し、貴金属粒子の移動を化学的に抑制する。また、この貴金属粒子2を第1の化合物3とを第2の化合物4で覆い、内包する形態とすることにより、貴金属粒子2の移動を物理的に抑制する。更に、この第2の化合物4により隔てられた区画内に貴金属粒子2と第1の化合物3とを含むことにより、この第2の化合物4により隔てられた区画を越えて第1の化合物3が接触し凝集することを抑制する。これらのことから、排気ガス浄化用触媒1は、製造コストや環境負荷を大きくすることなく、貴金属粒子2の凝集による触媒活性低下を防止することができ、また、第1の化合物3による貴金属粒子2の活性向上効果を維持することができる。   In the exhaust gas purifying catalyst 1 having such a structure, the noble metal particles 2 and the first compound 3 are brought into contact with each other and supported, whereby the first compound 3 acts as an anchor agent for chemical bonding. Chemically inhibits the movement of particles. Moreover, the movement of the noble metal particle 2 is physically suppressed by covering the noble metal particle 2 with the first compound 3 with the second compound 4 and enclosing it. Further, by containing the noble metal particles 2 and the first compound 3 in the section separated by the second compound 4, the first compound 3 crosses the section separated by the second compound 4. Suppresses contact and aggregation. For these reasons, the exhaust gas purifying catalyst 1 can prevent a decrease in catalytic activity due to aggregation of the noble metal particles 2 without increasing the manufacturing cost and environmental load, and the noble metal particles due to the first compound 3 can be prevented. 2 activity improvement effect can be maintained.

本発明は、第1の化合物が、Tiを主成分とすることを特徴の一つとしている。第1の化合物が、Ceを主成分とした酸化物よりなる従来の排気ガス浄化用触媒では、ストイキオメトリーよりもリーン側で運転されるガソリン直噴エンジン及びディーゼルエンジンに適用したときに、雰囲気中に大量の酸素が存在するため、近傍の貴金属に対し、低温時には過度の酸素吸着による吸着被毒、高温時は過度の酸素放出による貴金属酸化が生じ、性能低下が起きることがある。   The present invention is characterized in that the first compound contains Ti as a main component. In a conventional exhaust gas purifying catalyst in which the first compound is made of an oxide containing Ce as a main component, when applied to a gasoline direct-injection engine and a diesel engine operated on the lean side of stoichiometry, the atmosphere Since a large amount of oxygen is present in the inside, there is a possibility that a nearby noble metal may be adsorbed and poisoned by excessive oxygen adsorption at a low temperature, and noble metal oxidation may be caused by excessive oxygen release at a high temperature.

これに対して、本発明では、第1の化合物として、アンカー作用を有し、Ceと比較して酸素吸放出能が低く、かつCeと同様に表面が塩基性であるTiを用いる。このことにより、図1に示した構造を具備することで貴金属の耐久性向上を維持したままで、ストイキからリーンにかけての雰囲気下にて、排気ガスを酸化することで浄化することが求められる触媒の酸化性能が著しく向上する。特に、排気ガス成分中のHC、なかでも酸化浄化が難しいメタンを本発明の排気ガス浄化用触媒は効果的に酸化することができるため、その性能向上代は大きい。   On the other hand, in the present invention, Ti having an anchoring action, lower oxygen absorption / release capacity than Ce and having a basic surface like Ce is used as the first compound. Thus, a catalyst that is required to be purified by oxidizing the exhaust gas in an atmosphere from stoichiometric to lean while maintaining the durability improvement of the noble metal by having the structure shown in FIG. This significantly improves the oxidation performance. In particular, since the exhaust gas purifying catalyst of the present invention can effectively oxidize HC in exhaust gas components, especially methane, which is difficult to oxidize and purify, the performance improvement cost is large.

本発明の排気ガス浄化用触媒では、上述した触媒の酸化性能が著しく向上する理由については、必ずしも明らかではないが、第1の化合物がTiを主成分とする化合物であることによる、特に貴金属酸化の抑制によるものと考えられる。貴金属が例えばPtである場合には、酸化程度によってメタルPt、PtO、PtO2の状態に変化することが知られているが、これらの状態のなかで、メタルPt が排気ガスの酸化性能が最も高く、メタルPt→PtO→PtO2の順に酸化性能が低下する。このような貴金属の酸化状態は、反応雰囲気でも変化するが、貴金属粒子を担持する基材の物性、すなわち本発明における第1の化合物の物性によっても変化することが発明者らによって明らかとなった。特に担持する第1の化合物がCeを主成分とする酸化物である場合と比較して、Tiを主成分とする化合物である場合では、PtはメタルPtに近い電子状態を取りやすく、酸化活性が向上する。なお、この変化はXPSにより観測することが可能である。以上のことから、本発明では、Tiを第1の化合物として用いることで触媒の酸化活性を向上させることができる。 In the exhaust gas purifying catalyst of the present invention, the reason why the oxidation performance of the above-described catalyst is remarkably improved is not necessarily clear. However, the first compound is a compound mainly composed of Ti. This is thought to be due to the suppression of For example, when the precious metal is Pt, it is known that the state changes to the state of metal Pt, PtO, PtO 2 depending on the degree of oxidation. Among these states, the metal Pt has the highest oxidation performance of exhaust gas. The oxidation performance decreases in the order of metal Pt → PtO → PtO 2 . The inventors have clarified that the oxidation state of such a noble metal also changes in the reaction atmosphere, but also changes depending on the physical properties of the substrate supporting the noble metal particles, that is, the physical properties of the first compound in the present invention. . In particular, in the case where the first compound supported is a compound containing Ti as the main component, Pt tends to take an electronic state close to that of metal Pt, as compared with the case where it is a compound containing Ce as the main component, and oxidation activity. Will improve. This change can be observed by XPS. From the above, in the present invention, the oxidation activity of the catalyst can be improved by using Ti as the first compound.

貴金属は、触媒作用を有し、排気ガス浄化用触媒に用いられて好適な[Pt、Pd及びRh]の中から選ばれる少なくとも1つの元素とする。   The noble metal has a catalytic action and is at least one element selected from [Pt, Pd and Rh] suitable for use in an exhaust gas purifying catalyst.

第2の化合物は、耐熱性を有し、かつ、この第2の化合物4に内包される貴金属粒子2に排気ガスを到達させる細孔を形成可能な材料として、[Al及びSi]から選ばれる1つ以上を主成分とする化合物とする。具体的には、Al2O3、SiO2、Al−Si複合酸化物などが適用できる。また第2の化合物は、Al2O3とSiO2との混合物であってもよい。 The second compound is selected from [Al and Si] as a material having heat resistance and capable of forming pores that allow the exhaust gas to reach the noble metal particles 2 included in the second compound 4. A compound having one or more as a main component. Specifically, Al 2 O 3 , SiO 2 , Al—Si composite oxide and the like can be applied. The second compound may be a mixture of Al 2 O 3 and SiO 2 .

本発明の排気ガス浄化用触媒のユニット、すなわち、貴金属は当該第1の化合物に担持され、この貴金属が担持された第1の化合物は当該第2の化合物に内包されて、当該貴金属が担持された第1の化合物同士がこの第2の化合物により隔てられた構造のユニットは、当該ユニット内の貴金属の量が、8×10−20モル以下であるユニットを含むことが好ましい。 The exhaust gas purifying catalyst unit of the present invention, that is, the noble metal is supported on the first compound, the first compound on which the noble metal is supported is encapsulated in the second compound, and the noble metal is supported on the first compound. The unit having a structure in which the first compounds are separated from each other by the second compound preferably includes a unit in which the amount of the noble metal in the unit is 8 × 10 −20 mol or less.

図2は、本発明の排気ガス浄化用触媒のユニットの例を示す模式図である。同図に示す排気ガス浄化用触媒1は、貴金属粒子2と、この貴金属粒子2を担持する第1の化合物3と、貴金属粒子2及び第1の化合物3を内包する第2の化合物4とからなる点は図1に示した排気ガス浄化用触媒1と同一である。そして第2の化合物4により隔てられた区画内に、貴金属粒子2と第1の化合物3とが種々の態様で含まれている。   FIG. 2 is a schematic view showing an example of a unit of the exhaust gas purifying catalyst of the present invention. The exhaust gas purifying catalyst 1 shown in FIG. 1 includes noble metal particles 2, a first compound 3 supporting the noble metal particles 2, and a second compound 4 containing the noble metal particles 2 and the first compound 3. This point is the same as the exhaust gas purifying catalyst 1 shown in FIG. The noble metal particles 2 and the first compound 3 are contained in various modes in the compartments separated by the second compound 4.

図2において、第2の化合物4により隔てられた構造のユニットのうち、ユニットU1では、単体の貴金属粒子2を担持した単体の第1の化合物3が含まれている。またユニットU2では、複数の貴金属粒子2を担持している複数個の第1の化合物3が、凝集した集合体(二次粒子)で含まれている。またユニットU3〜U6では、複数の貴金属粒子2を担持している単体の第1の化合物3が、種々の粒径で含まれている。   In FIG. 2, among the units having a structure separated by the second compound 4, the unit U <b> 1 includes a single first compound 3 carrying a single noble metal particle 2. Further, in the unit U2, a plurality of first compounds 3 carrying a plurality of noble metal particles 2 are contained as aggregates (secondary particles). In the units U3 to U6, a single first compound 3 carrying a plurality of noble metal particles 2 is contained in various particle sizes.

図2に示された排気ガス浄化用触媒1のユニットU1〜U6のいずれも、図1に示した排気ガス浄化用触媒1と同様に、第2の化合物4により隔てられた区画を越えて第1の化合物3が接触し凝集することが抑制される。したがって、図1に示した排気ガス浄化用触媒1と同様の効果を有している。   Each of the units U1 to U6 of the exhaust gas purifying catalyst 1 shown in FIG. 2 is the same as the exhaust gas purifying catalyst 1 shown in FIG. 1 beyond the section separated by the second compound 4. It is suppressed that 1 compound 3 contacts and aggregates. Therefore, it has the same effect as the exhaust gas purifying catalyst 1 shown in FIG.

この第2の化合物4により隔てられた構造のユニット内には、貴金属粒子を合計で8×10−20モル以下の量で含有することが好ましい。図2に示したように、第2の化合物4により隔てられた区画内に含まれる貴金属粒子2と第1の化合物3とは、種々の態様がある。排気ガス浄化用触媒が実用に供されたとき、雰囲気の高温などに起因してこれらの区画内で複数個の貴金属粒子2が移動して、互いに凝集する場合がある。この場合に、貴金属粒子2は、ユニットU1〜U6のいずれでも、アンカー剤としての第1の化合物3の効果によって第2の化合物4には移動せず、ユニット内でのみ一つ又は複数個の貴金属粒に凝集する。一つのユニットにおける貴金属粒子2の凝集前後の一例を模式的に図3(a)及び、(b)に示す。 In the unit having a structure separated by the second compound 4, it is preferable to contain precious metal particles in an amount of 8 × 10 −20 mol or less in total. As shown in FIG. 2, the noble metal particles 2 and the first compound 3 included in the compartments separated by the second compound 4 have various modes. When the exhaust gas purifying catalyst is put to practical use, a plurality of noble metal particles 2 may move in these compartments due to the high temperature of the atmosphere and agglomerate with each other. In this case, the precious metal particles 2 do not move to the second compound 4 due to the effect of the first compound 3 as the anchor agent in any of the units U1 to U6, and only one or a plurality of the precious metal particles 2 are present in the unit. Aggregates into noble metal particles. An example of before and after aggregation of the noble metal particles 2 in one unit is schematically shown in FIGS. 3 (a) and 3 (b).

ここに、貴金属粒が一つのユニット内で凝集したとしても、凝集した貴金属粒の粒径が10[nm]以下であれば、充分な触媒活性を示し、凝集による触媒活性の劣化を抑制することができる。図4は、触媒活性を有する貴金属としての白金やパラジウムについて、貴金属粒子径と貴金属表面積との関係を示すグラフである。なお、同図では貴金属が白金の場合とパラジウムの場合と、ほぼ同じ曲線を示すので、一つの曲線として示している。同図から明らかなように、貴金属の粒子径が10[nm]以下であれば粒子表面積が大きく、十分な活性が得られるので、凝集による触媒活性の劣化を抑制することができる。   Here, even if the noble metal particles are aggregated in one unit, if the particle size of the aggregated noble metal particles is 10 nm or less, sufficient catalytic activity is exhibited, and deterioration of the catalytic activity due to aggregation is suppressed. Can do. FIG. 4 is a graph showing the relationship between the noble metal particle diameter and the noble metal surface area for platinum or palladium as a noble metal having catalytic activity. In the figure, since the curves are almost the same when the noble metal is platinum and palladium, they are shown as one curve. As is clear from the figure, if the particle diameter of the noble metal is 10 [nm] or less, the particle surface area is large and sufficient activity can be obtained, so that deterioration of the catalyst activity due to aggregation can be suppressed.

図5は、触媒活性を有する貴金属としての白金やパラジウムについて、貴金属粒子径と貴金属の原子数との関係を示すグラフである。なお、同図では貴金属が白金の場合とパラジウムの場合と、ほぼ同じ曲線を示すので、一つの曲線として示している。同図から明らかなように、貴金属の粒子径が10[nm]であるときの原子数は約48000個であり、この値をモル数に換算すると約8×10−20モル以下の量になる。 FIG. 5 is a graph showing the relationship between the noble metal particle diameter and the number of noble metal atoms for platinum or palladium as a noble metal having catalytic activity. In the figure, since the curves are almost the same when the noble metal is platinum and palladium, they are shown as one curve. As is clear from the figure, the number of atoms when the particle diameter of the noble metal is 10 [nm] is about 48,000, and when this value is converted into the number of moles, the amount is about 8 × 10 −20 moles or less. .

これらの観点から、ユニットU1〜U6のいずれの態様であっても、ユニット内の貴金属量を制限し、8×10−20モル以下の量とすることで、ユニット内で1個に凝集しても、触媒活性の劣化を抑制することができる。 From these viewpoints, in any of the units U1 to U6, by limiting the amount of noble metal in the unit and making it an amount of 8 × 10 −20 mol or less, it aggregates into one in the unit. Also, it is possible to suppress the deterioration of the catalyst activity.

ユニット内に含まれる貴金属量を8×10−20モル以下に低減する手段としては、第1の化合物3の貴金属粒子2の担持濃度を下げること、又は貴金属粒子2を担持した第1の化合物3の粒径を小さくすることの、2つの手段が存在する。本発明では、これらの手段に限定しないが、実際の触媒製造を考えた場合には、前者の担持濃度を下げる方法では、所定の排気ガス浄化触媒の性能を維持するためには排気ガス浄化用触媒をコートしたハニカム担体の容積を増やさなければならず、したがって、触媒のコート量が通常の一桁多いようなコート量をハニカム担体へコートする必要があるため、現実的ではない。 As a means for reducing the amount of the noble metal contained in the unit to 8 × 10 −20 mol or less, the supporting concentration of the noble metal particles 2 of the first compound 3 is lowered, or the first compound 3 supporting the noble metal particles 2 is used. There are two means of reducing the particle size of the. In the present invention, although not limited to these means, when actual catalyst production is considered, the former method of lowering the supported concentration can be used for exhaust gas purification in order to maintain the performance of a predetermined exhaust gas purification catalyst. Since the volume of the honeycomb carrier coated with the catalyst has to be increased, and therefore, it is necessary to coat the honeycomb carrier with a coating amount that is usually an order of magnitude larger than that of the catalyst, it is not practical.

第1の化合物3の粒径に関して、メジアン粒径は、2[μm]以下とすることが好ましい。本発明において、独立に分散した第1の化合物3の粒径は、二次粒径のことをいう。第1の化合物3は、貴金属粒子2と接触して貴金属粒子2の移動を抑制するアンカー剤としての機能を有している。このアンカー剤のアンカー効果は、第1の化合物3自身の大きさに影響を受ける。従来の排気ガス浄化用触媒のように、単に粉末状の第1の化合物、例えばTi酸化物などに貴金属を含浸担持し、アルミナ中に分散させても上記の充分な貴金属凝集抑制効果を発揮することが難しい。例えば、従来のボールミルなどによる粉砕製法によって第1の化合物3の粒子を得る場合には、最小でも2〜3[μm]の粒径までしか得られない。このような最小でも2〜3[μm]の粒径を有する第1の化合物3粒子を用いた排気ガス浄化用触媒であって、実際のコージェライトハニカム担体へのコート量上限及び使用貴金属量から定められる量で貴金属粒子2をこの第1の化合物3粒子に担持させた排気ガス浄化用触媒は、高温、長時間での使用により、貴金属粒子2が数十[nm]にまで凝集し、触媒活性が劣化してしまう。したがって、実際の触媒に適用する際には、第2の化合物4により隔てられた区画内に含まれる第1の化合物3が、メジアン径が2[μm]以下の粒子径であることが好ましい。このような平均粒子径が2[μm]以下の粒子径の第1の化合物は、後で述べる製造方法の説明で詳述するが、貴金属を担持した第1の化合物について、微細なコロイドとしたり、2[μm]以下にまで粉砕可能な装置を用いた粉砕法を適宜適用したりすることにより得られる。 Regarding the particle diameter of the first compound 3, the median particle diameter is preferably 2 [μm] or less . In the present invention, the particle size of the first compound 3 dispersed independently refers to the secondary particle size. The first compound 3 has a function as an anchor agent that contacts the noble metal particles 2 and suppresses the movement of the noble metal particles 2. The anchor effect of this anchor agent is affected by the size of the first compound 3 itself. Like the conventional exhaust gas purifying catalyst, the above-mentioned sufficient precious metal aggregation suppressing effect is exhibited even when a noble metal is impregnated and supported on a powdery first compound such as Ti oxide and dispersed in alumina. It is difficult. For example, when the particles of the first compound 3 are obtained by a pulverization method using a conventional ball mill or the like, only a particle size of 2 to 3 [μm] is obtained at the minimum. An exhaust gas purifying catalyst using three particles of the first compound having a particle size of 2 to 3 [μm] at the minimum, based on the actual upper limit of the coating amount on the cordierite honeycomb carrier and the amount of precious metal used. The exhaust gas purifying catalyst in which the noble metal particles 2 are supported on the first compound 3 particles in a predetermined amount, the noble metal particles 2 aggregate to several tens [nm] when used for a long time at a high temperature. Activity will deteriorate. Therefore, when applied to an actual catalyst, it is preferable that the first compound 3 contained in the compartment separated by the second compound 4 has a median diameter of 2 [μm] or less. The first compound having an average particle size of 2 [μm] or less will be described in detail in the description of the production method described later. The first compound carrying a noble metal may be made into a fine colloid. It can be obtained by appropriately applying a pulverization method using an apparatus capable of pulverizing to 2 [μm] or less.

第1の化合物3の平均粒径の下限については、工業的な製造プロセスにより作製可能な第1の化合物3の粒径として定められ、特に限定されない。   The lower limit of the average particle size of the first compound 3 is determined as the particle size of the first compound 3 that can be produced by an industrial manufacturing process, and is not particularly limited.

Tiを主成分とする本発明に係る第1の化合物は、より具体的には、Tiを含む酸化物であることが好ましい。Tiを含む酸化物は、金属元素がTiのみである酸化物、すなわちTiO2等のTi酸化物であっても良いが、Tiと第3の化合物との複合酸化物であり、かつ、この第3の化合物が、[Ce、Zr、Ba、Mg、W、Nd及びY]から選ばれる少なくとも1つの元素の化合物であることが、より好ましい。第1の化合物にはTiに加え、第3化合物を1種以上で添加することが可能である。[Ce、Zr、Ba、Mg、W、Nd及びY]は、いずれも、副成分として本発明の第1の化合物に添加して有効な成分である。第1の化合物中に、[Ce、Zr、Ba、Mg、W、Nd及びY]から選ばれる少なくとも1つの元素又はその化合物を添加することにより、表面塩基増による酸性物質の吸着促進や、これらの副成分の元素添加により第1の化合物の結晶構造安定化を図ることによる耐熱性の向上などの効果が得られる。この第3の化合物としては、例えば、CeO2、ZrO2、BaO、MgO、WO3、Nd2O3、Y2O3などの、副成分の元素の酸化物がある。また、この第3の化合物の、第1の化合物中における含有割合は、特に限定されないが、本発明では第1の化合物がTiを主成分とするのであるから、第3の化合物は50mol%未満である。 More specifically, the first compound according to the present invention containing Ti as a main component is preferably an oxide containing Ti. The oxide containing Ti may be an oxide in which the metal element is only Ti, that is, a Ti oxide such as TiO 2 , but is a composite oxide of Ti and a third compound. More preferably, the compound 3 is a compound of at least one element selected from [Ce, Zr, Ba, Mg, W, Nd and Y]. In addition to Ti, it is possible to add one or more third compounds to the first compound. [Ce, Zr, Ba, Mg, W, Nd and Y] are all effective components added to the first compound of the present invention as subcomponents. By adding at least one element selected from [Ce, Zr, Ba, Mg, W, Nd and Y] or a compound thereof to the first compound, it is possible to promote the adsorption of acidic substances by increasing the surface base. The effect of improving the heat resistance and the like by stabilizing the crystal structure of the first compound can be obtained by adding the subcomponent element. Examples of the third compound include oxides of subcomponent elements such as CeO 2 , ZrO 2 , BaO, MgO, WO 3 , Nd 2 O 3 , and Y 2 O 3 . Further, the content ratio of the third compound in the first compound is not particularly limited, but in the present invention, the first compound is mainly composed of Ti, and therefore the third compound is less than 50 mol%. It is.

また、第1の化合物は、上述したTi酸化物と第3の化合物との複合酸化物のみならず、Ti酸化物と第3の化合物との混合物であってもよい。   Further, the first compound is not limited to the composite oxide of the Ti oxide and the third compound described above, but may be a mixture of the Ti oxide and the third compound.

第2の化合物は、[Al及びSi]から選ばれる1つ以上を主成分とし、更に[La、Zr、Ce、Y及びNd]から選ばれる1つ以上を含むことができる。[La、Zr、Ce、Y及びNd]は、いずれも、副成分として本発明の第2の化合物に添加して有効な成分である。第2の化合物中に、[La、Zr、Ce、Y及びNd]から選ばれる少なくとも1つの元素又はその化合物を添加することにより、表面塩基増による酸性物質の吸着促進や、これらの副成分の元素添加により第2の化合物の結晶構造安定化を図ることによる耐熱性の向上などの効果が得られる。第2の化合物に[La、Zr、Ce、Y及びNd] から選ばれる少なくとも1つの元素が添加されて、第2の化合物が[Al及びSi]から選ばれる1つ以上との複合酸化物よりなる場合に、当該複合酸化物の構成要素としての[La、Zr、Ce、Y及びNd]の酸化物の具体例としては、La2O3、ZrO2、CeO2、Y2O3、Nd2O3、などがある。また、この第2の化合物中における[La、Zr、Ce、Y及びNd] から選ばれる少なくとも1つの元素又はその化合物の含有割合は、特に限定されないが、本発明では第2の化合物が[Al及びSi]から選ばれる1つ以上を主成分とするのであるから、50mol%未満である。 The second compound contains as a main component one or more selected from [Al and Si], and may further include one or more selected from [La, Zr, Ce, Y, and Nd]. [La, Zr, Ce, Y and Nd] are all effective components added to the second compound of the present invention as subcomponents. By adding at least one element selected from [La, Zr, Ce, Y and Nd] or a compound thereof to the second compound, it is possible to promote adsorption of acidic substances by increasing the surface base, Effects such as improvement of heat resistance can be obtained by stabilizing the crystal structure of the second compound by adding the element. By adding at least one element selected from [La, Zr, Ce, Y and Nd] to the second compound, and the second compound is a composite oxide with one or more selected from [Al and Si] In this case, specific examples of oxides of [La, Zr, Ce, Y, and Nd] as constituent elements of the composite oxide include La 2 O 3 , ZrO 2 , CeO 2 , Y 2 O 3 , Nd 2 O 3 , etc. Further, the content ratio of at least one element selected from [La, Zr, Ce, Y, and Nd] in the second compound or the compound thereof is not particularly limited, but in the present invention, the second compound is [Al And Si]], the main component being one or more selected from Si].

次に、本発明の排気ガス浄化用触媒の製造方法について説明する。まず、第1の化合物上に貴金属を担持させる工程を行う。この第1の化合物上に貴金属を担持させる工程は、一つの例としては、貴金属が接触した第1の化合物を、1次粒子径が100nm以下のコロイド状にする工程とすることができる。また、別の例としては、第1の化合物の2次粒子集合体を微粒化して、貴金属が接触した第1の化合物の2次粒子径を2μm以下にする工程とすることができる。   Next, the manufacturing method of the exhaust gas purifying catalyst of the present invention will be described. First, a step of supporting a noble metal on the first compound is performed. The step of supporting the noble metal on the first compound can be, for example, a step of making the first compound in contact with the noble metal into a colloidal form having a primary particle diameter of 100 nm or less. As another example, the secondary particle aggregate of the first compound can be atomized so that the secondary particle diameter of the first compound in contact with the noble metal is 2 μm or less.

前者の、貴金属が接触した第1の化合物を、1次粒子径が100nm以下のコロイド状にする工程について以下述べる。この工程は、第1の化合物のコロイドを、市販のもの又は別途の調製により用意し、この第1の化合物のコロイドに貴金属を接触させる工程とすることができる。具体的には、第1の化合物のコロイドに、貴金属塩を加え分散させてからエタノール等の還元剤を利用して第1の化合物の表面上に貴金属を還元析出させることにより貴金属を接触させる。又は、第1の化合物のコロイドに、貴金属コロイドを加えることにより貴金属を接触させる。   The former step of making the first compound in contact with the noble metal into a colloidal form having a primary particle diameter of 100 nm or less will be described below. This step can be a step of preparing a colloid of the first compound commercially available or separately prepared, and bringing the noble metal into contact with the colloid of the first compound. Specifically, a noble metal salt is added to and dispersed in the colloid of the first compound, and then the noble metal is brought into contact by reducing and precipitating the noble metal on the surface of the first compound using a reducing agent such as ethanol. Alternatively, the noble metal is brought into contact by adding a noble metal colloid to the colloid of the first compound.

図6に示すこの工程の説明図において、矢印より左側には、この工程によって、第1の化合物3に、貴金属粒子2が接触しているところを模式的に示している。なお、この工程では、第1の化合物のコロイドを、貴金属粒子2の接触の前に分散用保護材料で包むこともできるし、また、貴金属粒子の接触の後に分散用保護材料で包むこともできる。図6の矢印より右側には、貴金属粒子2が接触した第1の化合物3を包んで分散用保護材料7が形成されているところを模式的に示している。この分散用保護材料7は、たとえば高分子化合物(ポリマー)や硝酸や酢酸などであり、貴金属粒子2が接触した第1の化合物3の凝集をより効果的に抑制することができるが、本発明の排気ガス浄化用触媒の製造方法においては、必要に応じて使用すればよく、必須のものではない。   In the explanatory diagram of this process shown in FIG. 6, the place where the noble metal particles 2 are in contact with the first compound 3 by this process is schematically shown on the left side of the arrow. In this step, the colloid of the first compound can be wrapped with the protective material for dispersion before the contact with the noble metal particles 2 or can be wrapped with the protective material for dispersion after the contact with the noble metal particles. . The right side of the arrow in FIG. 6 schematically shows that the protective material 7 for dispersion is formed so as to wrap the first compound 3 in contact with the noble metal particles 2. The dispersion protective material 7 is, for example, a polymer compound (polymer), nitric acid, acetic acid, or the like, and can more effectively suppress the aggregation of the first compound 3 in contact with the noble metal particles 2. In the method for producing an exhaust gas purifying catalyst, it may be used as necessary and is not essential.

上記工程により、この貴金属が接触した第1の化合物は、コロイド溶液中で均一に分散するので、貴金属粒子が接触した第1の化合物同士が、溶液中で凝集することが抑制される。これにより、後工程を経て製造された排気ガス浄化用触媒の第1の化合物の二次粒径を、平均粒径で2μm以下に容易にすることができる。排気ガス浄化用触媒の第1の化合物の二次粒径を、平均粒径で2μm以下にするためには、当該コロイドの1次粒子径が100nm以下であることが好ましい。   By the above process, the first compound in contact with the noble metal is uniformly dispersed in the colloidal solution, so that the first compounds in contact with the noble metal particles are prevented from aggregating in the solution. Thereby, the secondary particle diameter of the first compound of the exhaust gas purifying catalyst manufactured through the post-process can be easily reduced to 2 μm or less in average particle diameter. In order to set the secondary particle size of the first compound of the exhaust gas purifying catalyst to an average particle size of 2 μm or less, the primary particle size of the colloid is preferably 100 nm or less.

次に、第1の化合物上に貴金属を担持させる工程として先に挙げたうち、後者である、第1の化合物の2次粒子集合体を微粒化して、貴金属が接触した第1の化合物の2次粒子径を2μm以下にする工程について述べる。この工程は、第1の化合物について、ミクロンオーダーの粒径を有するものを用意し、その第1の化合物を破砕することと、第1の化合物上に貴金属を担持させることとの組み合わせからなる。この第1の化合物の破砕と、第1の化合物上への貴金属の担持との順序は特に限定されない。例えば、第1の化合物上に貴金属粒子を担持させた後に、破砕することができる。また、第1の化合物を粉砕中に、貴金属粒子を担持させることもできる。更に、第1の化合物を粉砕した後に、貴金属粒子を担持させることもできる。   Next, among the steps mentioned above as the step of supporting the noble metal on the first compound, the latter, the second particle aggregate of the first compound, is atomized, and 2 of the first compound in contact with the noble metal is contacted. A process for setting the next particle size to 2 μm or less will be described. This step is a combination of preparing a first compound having a particle size on the order of microns, crushing the first compound, and supporting a noble metal on the first compound. The order of crushing the first compound and supporting the noble metal on the first compound is not particularly limited. For example, after precious metal particles are supported on the first compound, they can be crushed. In addition, noble metal particles can be supported during pulverization of the first compound. Furthermore, after pulverizing the first compound, the noble metal particles can be supported.

この第1の化合物への貴金属粒子の担持方法は、含浸法、噴霧法、混練法などを適宜用いることが可能である。それ以外にも、貴金属の前駆体塩や貴金属コロイドと、第1の化合物の前駆体塩とを水溶液中などで混合し、しかる後に第1の化合物の前駆体塩を不溶化し、溶媒を除去した後に焼成することで、貴金属の一部を第1の化合物中に包接する方法であってもよい。   As a method for supporting the noble metal particles on the first compound, an impregnation method, a spray method, a kneading method, or the like can be appropriately used. In addition, the precursor salt of the noble metal or the noble metal colloid and the precursor salt of the first compound are mixed in an aqueous solution, and then the precursor salt of the first compound is insolubilized and the solvent is removed. A method in which a part of the noble metal is included in the first compound by firing later may be used.

この第1の化合物の破砕方法は、振動式ボールミル、遊星式ボールミル、ビーズミル、ジェットミルなどのような粉砕機を用いて、湿式粉砕、乾式粉砕あるいは超音波粉砕など、第1の化合物の二次粒子径を2μm以下に可能な粉砕方法を適宜用いることができる。第1の化合物を粉砕することにより、本発明の製造方法により最終的に得られた排気ガス浄化用触媒の第1の化合物の2次粒径を2μm以下とすることができる。   The first compound is crushed by using a pulverizer such as a vibrating ball mill, a planetary ball mill, a bead mill, a jet mill, etc., and using a secondary pulverization method such as wet pulverization, dry pulverization, or ultrasonic pulverization. A pulverization method capable of reducing the particle diameter to 2 μm or less can be appropriately used. By grinding the first compound, the secondary particle size of the first compound of the exhaust gas purifying catalyst finally obtained by the production method of the present invention can be reduced to 2 μm or less.

粉砕後は、ポリエチレンイミド、ポリメタクリル酸などの高分子よりなる分散用保護材料と混合することでコロイド化することができる。このコロイド化により、貴金属を担持した第1の化合物の微細分散状態の安定化を図ることができる。このコロイド化の方法も、高分子保護材と混合するなど適宜用いることができる。その他にも、超音波分散などにより、次工程までの分散状態を維持することが可能である。   After pulverization, it can be colloided by mixing with a protective material for dispersion made of a polymer such as polyethyleneimide and polymethacrylic acid. This colloidalization can stabilize the fine dispersion state of the first compound carrying the noble metal. This colloidalization method can also be used as appropriate, for example, by mixing with a polymer protective material. In addition, it is possible to maintain the dispersion state up to the next step by ultrasonic dispersion or the like.

上記した第1の化合物の粉砕を行うことにより、貴金属が担持された第1の化合物は、数十nmから数百nm程度の微細な粒子となり、その後の工程で第2の化合物と包接される際に微細なユニットとして包接される。そのため、耐久後の第1の化合物同士の凝集が少なく、高活性の触媒を得ることができる。   By pulverizing the first compound, the first compound on which the noble metal is supported becomes fine particles of about several tens to several hundreds of nanometers, and is included in the second compound in the subsequent steps. It is included as a fine unit. Therefore, there is little aggregation of the first compounds after durability, and a highly active catalyst can be obtained.

次に、本発明の排気ガス浄化用触媒の製造方法においては、これまで説明した、第1の化合物上に貴金属を担持させる工程に次いで、微粒化した当該貴金属が接触した第1の化合物の周囲に、第2の化合物を形成させる工程を行う。   Next, in the method for producing an exhaust gas purifying catalyst of the present invention, after the step of supporting the noble metal on the first compound as described above, the periphery of the first compound in contact with the atomized noble metal is provided. And a step of forming a second compound.

この工程の一例を、図7の模式的な説明図を用いて説明する。同図の左側に図示されるような、貴金属粒子2が担持された微細な第1の化合物3に対して、第2の化合物の原料を加える。このことにより図7の中央に示されるように、貴金属粒子2が担持された微細な第1の化合物3の周囲に、第2の化合物の前駆体8を形成させる。形成させる方法は、含浸法でもよいし、また、包接法でもよい。次いで、図7の右側に示されるように、この第2の化合物の前駆体8が形成されたコロイド溶液の固形分を分離して、水分を留去して乾燥させ、その後に焼成することにより、第2の化合物の前駆体8を第2の化合物4にする。このようにして、本発明の排気ガス浄化用触媒が得られる。水分の留去は、バットなどでの静止状態での加熱による水分留去の他、マイクロ波などの電磁波加熱、エバポレータ等による減圧乾燥、スプレードライ等による噴霧加熱、フリーズドライ等による凍結乾燥等を適宜用いることが可能である。   An example of this process will be described with reference to the schematic explanatory view of FIG. The raw material of the second compound is added to the fine first compound 3 on which the noble metal particles 2 are supported as shown on the left side of the figure. As a result, as shown in the center of FIG. 7, the precursor 8 of the second compound is formed around the fine first compound 3 on which the noble metal particles 2 are supported. The forming method may be an impregnation method or an inclusion method. Next, as shown on the right side of FIG. 7, the solid content of the colloidal solution in which the precursor 8 of the second compound is formed is separated, dried by distilling off the water, and then calcined. The precursor 8 of the second compound is changed to the second compound 4. In this way, the exhaust gas purifying catalyst of the present invention is obtained. Distillation of water includes distillation of water by heating in a bat or the like, electromagnetic heating such as microwaves, vacuum drying using an evaporator, spray heating using spray drying, freeze drying using freeze drying, etc. It can be used as appropriate.

本発明の排気ガス浄化用触媒は、耐火性ハニカム担体等に塗布形成されて、実機のエンジンの排気ガス浄化に供される。   The exhaust gas purifying catalyst of the present invention is applied and formed on a refractory honeycomb carrier or the like and used for exhaust gas purification of an actual engine.

以下、本発明を実施例に基づいて具体的に説明する。   Hereinafter, the present invention will be specifically described based on examples.

[触媒粉末の製造方法]
表1に示す実施例1〜6及び比較例1〜2の触媒を作製した。これらの触媒の製造方法は、以下に述べるとおりである。

Figure 0005526502
[Method for producing catalyst powder]
Catalysts of Examples 1 to 6 and Comparative Examples 1 and 2 shown in Table 1 were prepared. The production methods of these catalysts are as described below.
Figure 0005526502

〔実施例1〕
第1の化合物の原料として市販の針状ルチルTiO2(1次粒径3[μm])を、湿式粉砕機にて純水中で粉砕し、レーザ散乱式粒度分布計にて測定されたメジアン径が200[nm]とした。この粉砕後の第1の化合物を含むスラリ中にジニトロジアミンPt水溶液(Pt濃度8.47[wt%])を分散させ、約2時間攪拌してPtが接触した第1の化合物を含むスラリを得た。その一方でベーマイト及び硝酸セリウム、硝酸酸化ジルコニウム、純水を混合したベーマイトスラリを得た。このスラリと、先ほどのPtが接触した第1の化合物を含むスラリとを混合し、高速攪拌機にて攪拌した。
[Example 1]
Commercially available acicular rutile TiO 2 (primary particle size 3 [μm]) as a raw material for the first compound was pulverized in pure water with a wet pulverizer and measured with a laser scattering particle size distribution meter. The diameter was 200 [nm]. A dinitrodiamine Pt aqueous solution (Pt concentration of 8.47 [wt%]) was dispersed in the pulverized slurry containing the first compound, and stirred for about 2 hours to obtain a slurry containing the first compound in contact with Pt. . On the other hand, boehmite slurry in which boehmite, cerium nitrate, zirconium nitrate oxide and pure water were mixed was obtained. This slurry was mixed with the slurry containing the first compound in contact with the Pt, and stirred with a high-speed stirrer.

攪拌後の当該スラリの水分を5%以下まで留去し、150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   The water in the slurry after stirring was distilled off to 5% or less, dried at 150 [° C.] for 12 hours, and then fired at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPt粒子が第1の化合物のTiO2に担持され、更に第2の化合物のCe−Zr−AlOxで覆われた触媒を得た。なお、第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a catalyst in which Pt particles of noble metal were supported on TiO 2 of the first compound and further covered with Ce-Zr-AlOx of the second compound was obtained. In addition, the mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values shown in Table 1.

〔実施例2〕
第1の化合物の原料として共沈法により調整したTiO2−ZrO2複合化合物を、湿式粉砕機にて純水中で粉砕し、レーザ散乱式粒度分布計にて測定されたメジアン径が300[nm]とした。この粉砕後の第1の化合物を含むスラリ中に、ジニトロジアミンPt水溶液(Pt濃度8.47[wt%])を分散させ、約2時間攪拌した後に更に分散用保護材料としてPEI(ポリエチレンイミン)を溶液中に20[wt%]混合し、更に2時間攪拌することでコロイド化した。その一方でベーマイト及び硝酸酸化ランタン、純水を混合したベーマイトスラリを得た。このスラリと、先ほどのPtが接触した第1の化合物を含むスラリとを混合し、高速攪拌機にて攪拌した。
[Example 2]
A TiO 2 —ZrO 2 composite compound prepared by a coprecipitation method as a raw material for the first compound is pulverized in pure water by a wet pulverizer, and the median diameter measured by a laser scattering particle size distribution analyzer is 300 [ nm]. A dinitrodiamine Pt aqueous solution (Pt concentration of 8.47 [wt%]) is dispersed in the slurry containing the first compound after pulverization, and after stirring for about 2 hours, a PEI (polyethyleneimine) solution is further added as a protective material for dispersion. The mixture was mixed with 20 wt%, and further colloided by stirring for 2 hours. Meanwhile, boehmite slurry in which boehmite, lanthanum nitrate oxide and pure water were mixed was obtained. This slurry was mixed with the slurry containing the first compound in contact with the Pt, and stirred with a high-speed stirrer.

撹拌後の当該スラリの水分を5%以下まで留去し、150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   The water in the slurry after stirring was distilled off to 5% or less, dried at 150 [° C.] for 12 hours, and then fired at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPt粒子が第1の化合物のTiO2−ZrO2複合化合物に担持され、更に第2の化合物のLa−AlOxで覆われた触媒を得た。なお、第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a catalyst in which Pt particles of noble metal were supported on the TiO 2 —ZrO 2 composite compound of the first compound and covered with La—AlOx of the second compound was obtained. In addition, the mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values shown in Table 1.

〔実施例3〕
第1の化合物の原料として市販のチタニアゾル(1次粒径30[nm])と硝酸バリウムとに、ジニトロジアミンPt水溶液(Pt濃度8.47[wt%])を分散させ、約2時間攪拌してPtが接触した第1の化合物を含む懸濁液を得た。その一方でアルミニウムイソプロポキシドをヘキシレングリコール中に混合し、120[℃]のオイルバス中で溶解させた溶液を作成した。このアルミニウムイソプロポキシドのヘキシレングリコール溶液中に、先ほどの混合物の懸濁液を80[℃]の油浴中でゆっくりと滴下し、Ptとチタニアゾル、硝酸バリウムの周囲に水酸化アルミニウムを形成した。
Example 3
Disperse a dinitrodiamine Pt aqueous solution (Pt concentration 8.47 [wt%]) in commercially available titania sol (primary particle size 30 [nm]) and barium nitrate as raw materials for the first compound, stir for about 2 hours and stir Pt. A suspension containing the first compound contacted was obtained. On the other hand, aluminum isopropoxide was mixed in hexylene glycol to prepare a solution dissolved in an oil bath at 120 [° C.]. In this hexylene glycol solution of aluminum isopropoxide, the suspension of the previous mixture was slowly dropped in an oil bath of 80 [° C.] to form aluminum hydroxide around Pt, titania sol and barium nitrate. .

この後、減圧化にて攪拌しながら油浴温度をしだいに上げ、溶媒を留去した。得られた粉末を80[℃]で6時間、更に150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   Thereafter, the oil bath temperature was gradually raised while stirring under reduced pressure, and the solvent was distilled off. The obtained powder was dried at 80 [° C.] for 6 hours and further at 150 [° C.] for 12 hours, and then calcined at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPt粒子の周囲に第1の化合物のTiO2−BaO複合酸化物が存在し、更に第2の化合物のアルミナで覆われた触媒を得た。なお、第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a TiO 2 —BaO composite oxide of the first compound was present around the noble metal Pt particles, and a catalyst covered with alumina of the second compound was obtained. The mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values shown in Table 1.

〔実施例4〕
第1の化合物の原料として共沈法により調整したTiO2−CeO2複合化合物を湿式粉砕機にて純水中で粉砕し、レーザ散乱式粒度分布計にて測定されたメジアン径が350nmとした。この粉砕後の第1の化合物を含むスラリ中にジニトロジアミンPt水溶液(Pt濃度8.47[wt%])を分散させ、約2時間攪拌した。その一方でベーマイト及び硝酸イットリウム、純水を混合したベーマイトスラリを得た。このスラリと、先ほどのPtが接触した第1の化合物を含むスラリとを混合し、高速攪拌機にて攪拌した。
Example 4
A TiO 2 -CeO 2 composite compound prepared by a coprecipitation method as a raw material for the first compound was pulverized in pure water with a wet pulverizer, and the median diameter measured with a laser scattering particle size distribution meter was 350 nm. . A dinitrodiamine Pt aqueous solution (Pt concentration of 8.47 [wt%]) was dispersed in the slurry containing the first compound after pulverization, and the mixture was stirred for about 2 hours. Meanwhile, boehmite slurry in which boehmite, yttrium nitrate and pure water were mixed was obtained. This slurry was mixed with the slurry containing the first compound in contact with the Pt, and stirred with a high-speed stirrer.

攪拌後の当該スラリの水分を5%以下まで留去し、150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   The water in the slurry after stirring was distilled off to 5% or less, dried at 150 [° C.] for 12 hours, and then fired at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPt粒子が第1の化合物のTiO2−CeO2複合化合物に担持され、更に第2の化合物のY−AlOxで覆われた触媒を得た。なお、第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a catalyst in which Pt particles of noble metal were supported on the TiO 2 -CeO 2 composite compound of the first compound and covered with Y-AlOx of the second compound was obtained. In addition, the mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values shown in Table 1.

〔実施例5〕
第1の化合物の原料として市販のブロック状ルチルTiO2(1次粒径2[μm])及び硝酸マグネシウムを、湿式粉砕機にて純水中で粉砕し、レーザ散乱式粒度分布計にて測定されたメジアン径が250[nm]とした。この粉砕後の第1の化合物を含むスラリ中に硝酸Pd水溶液(Pd濃度20.71[wt%])を分散させ、約2時間攪拌しPdが接触した第1の化合物を含むスラリを得た。その一方でベーマイト及び硝酸ネオジム、純水を混合したベーマイトスラリを得た。このスラリと、先ほどのPdが接触した第1の化合物を含むスラリとを混合し、高速攪拌機にて攪拌した。
Example 5
Commercially available block-like rutile TiO 2 (primary particle size 2 [μm]) and magnesium nitrate as raw materials for the first compound are pulverized in pure water using a wet pulverizer and measured with a laser scattering particle size distribution analyzer. The median diameter was 250 [nm]. An aqueous Pd nitrate solution (Pd concentration 20.71 [wt%]) was dispersed in the slurry containing the first compound after pulverization, and stirred for about 2 hours to obtain a slurry containing the first compound in contact with Pd. On the other hand, boehmite slurry in which boehmite, neodymium nitrate and pure water were mixed was obtained. This slurry was mixed with the slurry containing the first compound in contact with Pd, and stirred with a high-speed stirrer.

攪拌後の当該スラリの水分を5%以下まで留去し、150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   The water in the slurry after stirring was distilled off to 5% or less, dried at 150 [° C.] for 12 hours, and then fired at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPd粒子が第1の化合物のTiO 2 −MgO複合化合物に担持され、更に第2の化合物のNd−AlOxで覆われた触媒を得た。なお、第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a catalyst in which Pd particles of noble metal were supported on the TiO 2 —MgO composite compound of the first compound and covered with Nd—AlOx of the second compound was obtained. In addition, the mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values shown in Table 1.

〔実施例6〕
第1の化合物の原料として市販のチタニアゾル(1次粒径30[nm])と硝酸ネオジムに硝酸Rh水溶液(Rh濃度8.36[wt%])を分散させ、約2時間攪拌してRhが接触した第1の化合物を含む懸濁液を得た。その一方でテトラエトキシシランをヘキシレングリコール中に混合し、120[℃]のオイルバス中で溶解させた溶液を作成した。このテトラエトキシシラン等のヘキシレングリコール溶液中に、先ほどの混合物の懸濁液を80[℃]の油浴中でゆっくりと滴下し、Rhとチタニアゾル、硝酸ネオジムの周囲にSiO2前駆体を形成した。
Example 6
As a raw material for the first compound, a commercially available titania sol (primary particle size 30 [nm]) and neodymium nitrate were dispersed in an aqueous Rh nitrate solution (Rh concentration 8.36 [wt%]), and stirred for about 2 hours to contact Rh. A suspension containing the first compound was obtained. On the other hand, tetraethoxysilane was mixed in hexylene glycol to prepare a solution dissolved in an oil bath at 120 [° C.]. In this hexylene glycol solution such as tetraethoxysilane, the suspension of the above mixture is slowly dropped in an oil bath at 80 [° C] to form a SiO 2 precursor around Rh, titania sol, and neodymium nitrate. did.

この後、減圧化にて攪拌しながら油浴温度をしだいに上げ、溶媒を留去した。得られた粉末を80[℃]で6時間、更に150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   Thereafter, the oil bath temperature was gradually raised while stirring under reduced pressure, and the solvent was distilled off. The obtained powder was dried at 80 [° C.] for 6 hours and further at 150 [° C.] for 12 hours, and then calcined at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のRh粒子の周囲に第1の化合物のTiO2−Nd2O3複合酸化物が存在し、更に第2の化合物のSiO2で覆われた触媒を得た。なお、第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a TiO 2 —Nd 2 O 3 composite oxide of the first compound was present around the noble metal Rh particles, and a catalyst covered with SiO 2 of the second compound was obtained. The mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values shown in Table 1.

〔比較例1〕
比較例1は、貴金属を担持する第1の化合物が、CeO2−ZrO2である例である。
[Comparative Example 1]
Comparative Example 1 is an example in which the first compound supporting a noble metal is CeO 2 —ZrO 2 .

第1の化合物の原料として市販のCeO2−ZrO2複合化合物(1次粒径30[nm])を湿式粉砕機にて純水中で粉砕し、レーザ散乱式粒度分布計にて測定されたメジアン径が200[nm]とした。この粉砕後の第1の化合物を含むスラリ中にジニトロジアミンPt水溶液(Pt濃度8.47[wt%])を分散させ、約2時間攪拌してPtが接触した第1の化合物を含むスラリを得た。その一方でベーマイト及び硝酸セリウム、硝酸酸化ジルコニウム、純水を混合したベーマイトスラリを得た。このスラリと、先ほどのPtが接触した第1の化合物を含むスラリとを混合し、高速攪拌機にて攪拌した。 A commercially available CeO 2 —ZrO 2 composite compound (primary particle size 30 [nm]) as a raw material for the first compound was pulverized in pure water with a wet pulverizer and measured with a laser scattering particle size distribution analyzer. The median diameter was 200 [nm]. A dinitrodiamine Pt aqueous solution (Pt concentration of 8.47 [wt%]) was dispersed in the slurry containing the first compound after pulverization, and stirred for about 2 hours to obtain a slurry containing the first compound in contact with Pt. . On the other hand, boehmite slurry in which boehmite, cerium nitrate, zirconium nitrate oxide and pure water were mixed was obtained. This slurry was mixed with the slurry containing the first compound in contact with the Pt, and stirred with a high-speed stirrer.

攪拌後の当該スラリの水分を5%以下まで留去し、150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。   The water in the slurry after stirring was distilled off to 5% or less, dried at 150 [° C.] for 12 hours, and then fired at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPt粒子が第1の化合物のCeO2ZrO 2 複合化合物に担持され、更に第2の化合物のCe−Zr−AlOxで覆われた触媒を得た。第1の化合物及び第2の化合物のそれぞれにおける、混合物の各成分のモル%は表1中の値となるよう調整した。 As a result, a catalyst in which Pt particles of noble metal were supported on the CeO 2 —ZrO 2 composite compound of the first compound and further covered with Ce—Zr—AlOx of the second compound was obtained. The mol% of each component of the mixture in each of the first compound and the second compound was adjusted to the values in Table 1.

〔比較例2〕
比較例2は、第2の化合物を有していない、従来の一般的な触媒の例である。
[Comparative Example 2]
Comparative Example 2 is an example of a conventional general catalyst that does not have the second compound.

市販のAl2O3(1次粒径3[μm])をジニトロジアミンPt水溶液(Pt濃度8.47[wt%]及び純水中に分散させ、約2時間攪拌した後、水分を5%以下まで留去し、150[℃]で12時間乾燥した後に、400[℃]で1時間空気気流下で焼成した。 Commercially available Al 2 O 3 (primary particle size 3 [μm]) is dispersed in dinitrodiamine Pt aqueous solution (Pt concentration 8.47 [wt%]) and pure water, stirred for about 2 hours, and then the water content is reduced to below 5% After distilling off and drying at 150 [° C.] for 12 hours, firing was performed at 400 [° C.] for 1 hour in an air stream.

これにより貴金属のPt粒子が担体のAl2O3に担持された触媒を得た。なお、比較例2では、担体におけるアルミナのモル%は表1中の値のとおり100%であった。 Thus, a catalyst in which noble metal Pt particles were supported on Al 2 O 3 as a carrier was obtained. In Comparative Example 2, the mol% of alumina in the carrier was 100% as shown in Table 1.

[耐久条件]
以上のようにして製造された実施例1〜6及び比較例1〜2の触媒粉末を、それぞれ700[℃]で5[hr] 空気気流下にて焼成を行った。
[Durability conditions]
The catalyst powders of Examples 1 to 6 and Comparative Examples 1 and 2 produced as described above were calcined at 700 [° C.] and 5 [hr] in an air stream.

〔触媒性能評価〕
上記の耐久処理後の各触媒について、日本ベル株式会社製の触媒反応装置TPD-1-ATを用いて、表2に示す反応ガス組成、ガス流量条件で模擬排出ガスを流通させ、400[℃]における装置入側及び出側のCH4濃度から、実施例1〜6及び比較例1〜2の排気ガス浄化用触媒それぞれの400[℃]におけるCH4転化率(ηCH4)[%]を算出した。なお、試料量は0.1gとし、検出器はQ-MASSにて行った。このCH4転化率の値を表1に併記する。

Figure 0005526502
[Catalyst performance evaluation]
About each catalyst after the above-mentioned endurance treatment, simulated exhaust gas was circulated with the reaction gas composition and gas flow rate conditions shown in Table 2 using a catalytic reactor TPD-1-AT manufactured by Bell Japan Co., Ltd. ], The CH 4 conversion rate (ηCH 4 ) [%] at 400 [° C.] of each of the exhaust gas purifying catalysts of Examples 1 to 6 and Comparative Examples 1 and 2 is calculated from the CH 4 concentration on the inlet side and the outlet side of Calculated. The sample amount was 0.1 g, and the detector was Q-MASS. The CH 4 conversion values are also shown in Table 1.
Figure 0005526502

表1から明らかなように、実施例1〜6の触媒粉末は、比較例1〜2の触媒粉末と比べて、耐久処理後のCH4転化率が格段に優れている。これは、第1の化合物がTiを含む酸化物であることから、特にCH4に対する転化率が向上したものと考えられる。 As can be seen from Table 1, the catalyst powders of Examples 1 to 6 are much more excellent in CH 4 conversion after the durability treatment than the catalyst powders of Comparative Examples 1 and 2. This is presumably because the conversion ratio with respect to CH 4 is particularly improved because the first compound is an oxide containing Ti.

以上、本発明者らによってなされた発明を適用した実施の形態について説明したが、この実施の形態による本発明の開示の一部をなす論述及び図面により本発明は限定されることはない。すなわち、上記実施の形態に基づいて当業者等によりなされる他の実施の形態、実施例及び運用技術等は全て本発明の範疇に含まれることは勿論であることを付け加えておく。   As mentioned above, although the embodiment to which the invention made by the present inventors was applied has been described, the present invention is not limited by the description and the drawings that form part of the disclosure of the present invention according to this embodiment. That is, it should be added that other embodiments, examples, operation techniques, and the like made by those skilled in the art based on the above embodiments are all included in the scope of the present invention.

本発明の実施形態となる排気ガス浄化用触媒の構成を示す模式図である。It is a schematic diagram which shows the structure of the exhaust gas purification catalyst used as embodiment of this invention. 本発明の別の実施形態となる排気ガス浄化用触媒の構成を示す模式図である。It is a schematic diagram which shows the structure of the exhaust gas purification catalyst which becomes another embodiment of this invention. 一つのユニットにおける貴金属粒子2の凝集前後の一例を示す模式図である。It is a schematic diagram which shows an example before and behind aggregation of the noble metal particle 2 in one unit. 貴金属粒子径と貴金属表面積との関係を示すグラフである。It is a graph which shows the relationship between a noble metal particle diameter and a noble metal surface area. 貴金属粒子径と貴金属の原子数との関係を示すグラフである。It is a graph which shows the relationship between a noble metal particle diameter and the number of atoms of a noble metal. 本発明の製造方法における工程の一例の説明図である。It is explanatory drawing of an example of the process in the manufacturing method of this invention. 本発明の製造方法における工程の一例の説明図である。It is explanatory drawing of an example of the process in the manufacturing method of this invention.

符号の説明Explanation of symbols

1 排気ガス浄化用触媒
2 貴金属粒子
3 第1の化合物
4 第2の化合物
DESCRIPTION OF SYMBOLS 1 Exhaust gas purification catalyst 2 Noble metal particle 3 1st compound 4 2nd compound

Claims (6)

貴金属と、第1の化合物と、第2の化合物からなり、前記貴金属は当該第1の化合物に担持され、前記貴金属が担持された第1の化合物は当該第2の化合物に内包されて、当該貴金属が担持された第1の化合物同士が前記第2の化合物により隔てられた構造のユニットを含み、かつ、
前記貴金属はPtからなり
前記第1の化合物はTiを主成分とし、かつ、TiO 、TiO −ZrO 複合化合物又はTiO −CeO 複合化合物からなり、
前記第2の化合物は[Al及びSi]から選ばれる1つ以上を主成分とすることを特徴とする排気ガス浄化用触媒。
A noble metal, a first compound, made from a second compound, the noble metal is supported on the first compound, the first compound in which the noble metal is supported is encapsulated in the second compounds, the noble metal comprises units of the supported first compounds to each other separated by the second compound structure, and,
The noble metal is made of Pt ,
Wherein said first compound is mainly composed of Ti, and consists TiO 2, TiO 2 -ZrO 2 complex compound or TiO 2 -CeO 2 composite compound,
The exhaust gas purifying catalyst, wherein the second compound contains one or more selected from [Al and Si] as a main component.
前記ユニット内の貴金属の量が、8×10−20モル以下であることを特徴とする請求項1に記載の排気ガス浄化用触媒。 The amount of the noble metal in the unit, an exhaust gas purifying catalyst according to claim 1, wherein the der Turkey 8 × 10 -20 mol or less. 独立して分散した前記第1の化合物のメジアン粒径が2μm以下であることを特徴とする請求項1又は2に記載の排気ガス浄化用触媒。   The exhaust gas purification catalyst according to claim 1 or 2, wherein the median particle size of the first compound dispersed independently is 2 µm or less. 前記第2の化合物は、更に[La、Zr、Ce、Y及びNd]から選ばれる1つ以上を含むことを特徴とする請求項1〜のいずれか1項に記載の排気ガス浄化用触媒。 The exhaust gas purification catalyst according to any one of claims 1 to 3 , wherein the second compound further includes one or more selected from [La, Zr, Ce, Y, and Nd]. . 請求項1〜のいずれか1項に記載の排気ガス浄化用触媒を製造する方法であって、
貴金属が接触した第1の化合物を、1次粒子径が100nm以下のコロイド状にする工程と、
次いで、コロイド状にした当該貴金属が接触した第1の化合物の周囲に、第2の化合物を形成させる工程と
を含むことを特徴とする排気ガス浄化用触媒の製造方法。
A method for producing the exhaust gas purifying catalyst according to any one of claims 1 to 4 ,
Making the first compound in contact with the noble metal colloidal with a primary particle size of 100 nm or less;
And a step of forming a second compound around the first compound in contact with the colloidal noble metal. A method for producing an exhaust gas purifying catalyst.
請求項1〜のいずれか1項に記載の排気ガス浄化用触媒を製造する方法であって、
第1の化合物の2次粒子集合体を微粒化して、貴金属が接触した第1の化合物の2次粒子径を2μm以下にする工程と、
次いで、微粒化した当該貴金属が接触した第1の化合物の周囲に、第2の化合物を形成させる工程と
を含むことを特徴とする排気ガス浄化用触媒の製造方法。
A method for producing the exhaust gas purifying catalyst according to any one of claims 1 to 4 ,
The step of atomizing the secondary particle aggregate of the first compound to make the secondary particle diameter of the first compound in contact with the noble metal 2 μm or less;
And a step of forming a second compound around the first compound in contact with the atomized noble metal. A method for producing an exhaust gas purifying catalyst, comprising:
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